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Oral Submission Presentation by Blake Foster - New Zealand ...

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EXECUTIVE SUMMARY<br />

The problem<br />

Wilding conifers have been invading Pukaki Downs station since the early 1960s . Initially, invasion was<br />

restricted to a short section of the lakeshore <strong>by</strong> the Homestead, but more extensive invasion started to<br />

take hold in the late 1980s / early 1990s. The main spreading species is Lodgepole or contorta pine<br />

(Pinus contorta), the country’s most vigorous spreading conifer. At the present time, wildings are<br />

approaching canopy closure over approximately 30-40% of the station, with much of the remaining area<br />

affected <strong>by</strong> widely scattered outlier trees (often accompanied <strong>by</strong> patches of fringe spread). If left<br />

unmanaged, wildings would dominate the majority of Pukaki Downs. Hence, the owners are attempting<br />

to manage the spread <strong>by</strong> containment within the areas least likely to spread further, and removal of<br />

wildings from areas with higher risk of distant spread.<br />

Client Initiative<br />

In April, 2010, Nick Ledgard (NL) of Scion in Christchurch was asked <strong>by</strong> <strong>Blake</strong> <strong>Foster</strong> of Pukaki Tourism<br />

Holdings Ltd to carry out a field inspection and write a report on the wilding conifer situation and<br />

management options on Pukaki Downs station. NL visited the station from May 30 – June 2, 2010, after<br />

which he wrote this report.<br />

The project<br />

The major objectives of this report are to describe:<br />

a) the history of conifer spread, its origin and present location<br />

b) the likely future spread risk and pattern if left unmanaged<br />

c) priority control areas for minimising spread risk beyond present locations (particularly off-station)<br />

d) options for containing conifers within the managed areas.<br />

e) areas with least spread risk which could be managed for carbon storage.<br />

Key Findings<br />

o The wilding conifer problem along the south-western shores of Lake Pukaki is well<br />

known, situated alongside a major tourist route (SH80). Unfortunately, it involves<br />

the most spread-prone conifer species, contorta pine.<br />

o Wildings have been spreading since the 1960s, but the area obviously affected<br />

has only increased significantly in the last 15 years. This has been largely<br />

triggered <strong>by</strong> spread from the lake-shore plantings carried out after the lake was<br />

raised in the early 1970s, although most of the contorta forests in the southeastern<br />

portion of Pukaki Downs originate from trees present before that time.<br />

o The pattern of spread likely in the future is well indicated <strong>by</strong> the pattern of spread<br />

over the last few decades. These show that spread is mainly to the south, driven<br />

<strong>by</strong> the prevailing strong northerly winds, but that occasionally a more northeasterly<br />

wind can pick up and carry seed high into the air and more to the west.<br />

o Such an event in the early 1990s gave rise to outlier wildings in the upper Twizel<br />

river catchment, which were allowed to mature and cone before they were<br />

removed in the mid 2000s, giving rise to the islands of fringe spread so obvious<br />

today.<br />

o The ‘one-off’ nature of this spread event indicates that once the Twizel river flats<br />

are cleared, they should not be re-invaded often and hence should not be too<br />

difficult to keep clear in the future – as long as any wilding trees which do establish<br />

are removed before age 5-6, when they begin coning.<br />

o This ‘stitch-in-time-saves-nine’ maxim must always be kept foremost in any<br />

management plan.<br />

o Within the wilding cleared zones, a containment area of trees will remain.<br />

o Removal sweeps outside the containment area will be needed at least every 4<br />

years for as long as seeding contorta pine trees remain in the locality.<br />

o The incidence of re-invasion, and need for timely removal, should be diminished <strong>by</strong><br />

the control and containment management options recommended below.<br />

(i)

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